This report contains low streamflow information for the Thompson-Okanagan Natural Resource Region. Please see the Provincial Drought Portal for information about provincial conditions. Data is provided as is and may be unverified and uncorrected. Users assume all responsibility for use and interpretation of data within.
Data is sourced from the Water Survey of Canada, and was analyzed by the BC River Forecast Centre for the Thompson-Okanagan Natural Resource Region. Questions regarding data analysis can be sent to the BC River Forecast Centre; questions regarding interpretation can be sent to Ryan Whitehouse, Senior Aquatic Ecologist or Christian St. Pierre, Ecosystems Specialist.
This report was generated on 09 September 2021, 15:33 PM.
7 Day average streamflow percentiles compare current stream flows (averaged over the last seven days) to the same seven day period in a site’s historic record. Streamflows are averaged over seven days to minimize the impact of short term fluctuations, and gives a better representation of the overall trend in streamflow. Percentiles give an indication of how likely a seven day streamflow value is; for example, the 50th percentile represents normal conditions, where a streamflow percentile of 10 indicates that this value has occurred only 10% of the time within the history of the site. Data is sourced from real-time and historic Water Survey of Canada data.
In general, a 7 day average streamflow value of:
The below map shows percentiles using both a rolling average over the last seven days of discharge as well as mean discharge over the last 24 hours.
Map data was updated on 09 September 2021, 15:33 PM.
The table below lists all stations with 7 day discharge percentiles below their 10th percentile. If a location is not listed here there are no immediate low streamflow concerns (i.e., 7 day discharge is > 10th percentile).
Regulation Status refers to whether flows are natural or regulated by human activities such as dams; this (as well as the Basin Area) were determined by the Water Survey of Canada.
Data was updated on 09 September 2021, 15:33 PM.| Station Name | ID | Regulation Status | Basin Area (km2) | Latest 7-Day Discharge (m3/s) | Percentile Category - 7 Day Discharge | Percentile - 7 Day Discharge | Last 24 hour Discharge (m3/s) | Percentile - Last 24 Hour Discharge | Percentile Category - Last 24 Hour Discharge |
|---|---|---|---|---|---|---|---|---|---|
| SEYMOUR RIVER NEAR SEYMOUR ARM | 08LE027 | Natural | 8.05e+02 | 10.23 | Lowest Recorded | 0 | 10.50 | 0 | Lowest Recorded |
| THOMPSON RIVER NEAR SAVONA | 08LF033 | Natural | 3.91e+04 | 396.06 | Lowest Recorded | 0 | 380.02 | 0 | Lowest Recorded |
| FRASER RIVER AT BIG BAR CREEK | 08MD013 | Regulated | 1.46e+05 | 1039.48 | Lowest Recorded | 0 | 987.69 | 0 | Lowest Recorded |
| HEDLEY CREEK NEAR THE MOUTH | 08NL050 | Natural | 3.88e+02 | 0.15 | Lowest Recorded | 0 | 0.13 | 0 | Lowest Recorded |
| CAMP CREEK AT MOUTH NEAR THIRSK | 08NM134 | Natural | 3.46e+01 | 0.01 | Lowest Recorded | 0 | 0.01 | 0 | Lowest Recorded |
| PEARSON CREEK NEAR THE MOUTH | 08NM172 | Natural | 7.36e+01 | 0.08 | Lowest Recorded | 0 | 0.07 | 0 | Lowest Recorded |
| NORTH THOMPSON RIVER AT MCLURE | 08LB064 | Natural | 1.96e+04 | 218.63 | Lowest Recorded | 0 | 212.77 | 2 | 0-2nd Percentile |
| DENNIS CREEK NEAR 1780 METRE CONTOUR | 08NM242 | Natural | 3.73e+00 | 0.00 | Lowest Recorded | 0 | 0.00 | 3 | 2-5th Percentile |
| HURLEY RIVER BELOW LONE GOAT CREEK | 08ME027 | Natural | 3.12e+02 | 8.36 | Lowest Recorded | 0 | 11.18 | 60 | 30-75th Percentile |
| CLEARWATER RIVER NEAR CLEARWATER STATION | 08LA001 | Natural | 1.03e+04 | 112.75 | 0-2nd Percentile | 2 | 107.31 | 0 | Lowest Recorded |
| FISHTRAP CREEK NEAR MCLURE | 08LB024 | Natural | 1.35e+02 | 0.05 | 0-2nd Percentile | 2 | 0.05 | 2 | 0-2nd Percentile |
| TWO FORTY CREEK NEAR PENTICTON | 08NM240 | Natural | 4.94e+00 | 0.00 | 2-5th Percentile | 3 | 0.00 | 3 | 2-5th Percentile |
| THOMPSON RIVER NEAR SPENCES BRIDGE | 08LF051 | Natural | 5.54e+04 | 422.87 | 2-5th Percentile | 3 | 405.13 | 3 | 2-5th Percentile |
| EAGLE RIVER NEAR MALAKWA | 08LE024 | Natural | 9.32e+02 | 12.30 | 2-5th Percentile | 3 | 12.15 | 6 | 5-10th Percentile |
| VASEUX CREEK ABOVE SOLCO CREEK | 08NM171 | Natural | 1.17e+02 | 0.05 | 2-5th Percentile | 4 | 0.05 | 4 | 2-5th Percentile |
| WEST KETTLE RIVER NEAR MCCULLOCH | 08NN015 | Natural | 2.33e+02 | 0.12 | 5-10th Percentile | 6 | 0.09 | 3 | 2-5th Percentile |
| FRASER RIVER ABOVE TEXAS CREEK | 08MF040 | Regulated | 1.54e+05 | 1164.47 | 5-10th Percentile | 6 | 1084.22 | 4 | 2-5th Percentile |
| SALMON RIVER AT FALKLAND | 08LE020 | Regulated | 1.03e+03 | 0.48 | 5-10th Percentile | 6 | 0.48 | 8 | 5-10th Percentile |
| INKANEEP CREEK NEAR THE MOUTH | 08NM200 | Regulated | 2.27e+02 | 0.03 | 5-10th Percentile | 7 | 0.03 | 7 | 5-10th Percentile |
| NICOLA RIVER AT OUTLET OF NICOLA LAKE | 08LG065 | Regulated | 2.96e+03 | 1.74 | 5-10th Percentile | 8 | 1.74 | 18 | 10-20th Percentile |
| YALAKOM RIVER ABOVE ORE CREEK | 08ME025 | Natural | 5.81e+02 | 3.48 | 5-10th Percentile | 8 | 3.56 | 24 | 20-30th Percentile |
| NORTH THOMPSON RIVER AT BIRCH ISLAND | 08LB047 | Natural | 4.49e+03 | 103.09 | 5-10th Percentile | 8 | 114.61 | 33 | 30-75th Percentile |
Environmental flow needs for fish during the summer will range from juvenile rearing flows near 10-20% (preferred) Long-Term Mean Annual Discharge (LT MAD) to adult salmon/char passage flows (>20% LT MAD) required prior to spawning. Sub-standard flows (<10% LT MAD) can affect fish populations by reducing the area and quality of riffle habitats that generate fish food and aeration. Flows nearing 5% LT MAD are considered sub-optimal for fish rearing and migration, indicate a degradation of instream habitat and may require restrictions on water use. A map of realtime streamflow data can be accessed at the BC River Forecast Centre website. LT MAD values were calculated by dividing the 7 day mean discharge by the mean annual discharge (MAD) calculated from historic data. MAD values were calculated for stations with at least 5 years of data in the historic record only from years with complete data using the R package fasstr.
Map data was updated on 09 September 2021, 15:33 PM.
Any stations with LT MAD values of less than or equal to 20% LT MAD are shown in the table below; sites below 5% MAD and 10% MAD are highlighted. The report shows conditions as of today.
Regulation Status refers to whether flows are natural or regulated by human activities such as dams; this (as well as the Basin Area) were determined by the Water Survey of Canada.
Data was updated on 09 September 2021, 15:33 PM.
| Station Name | ID | Regulation Status | Basin Area (km2) | MAD (m3/s) | Latest 7 Day Discharge (m3/s) | % MAD | Last 24 hour Discharge (m3/s) | % MAD (24 hour Q) |
|---|---|---|---|---|---|---|---|---|
| DENNIS CREEK NEAR 1780 METRE CONTOUR | 08NM242 | Natural | 3.73 | 0.05 | 0.00 | 0 | 0.00 | % MAD (24 hour Q) |
| NICOLA RIVER AT OUTLET OF DOUGLAS LAKE | 08LG028 | Regulated | 1300.00 | 5.65 | 0.02 | 0.37 | 0.02 | % MAD (24 hour Q) |
| CLARK CREEK NEAR WINFIELD | 08NM146 | Natural | 15.30 | 0.08 | 0.00 | 1.27 | 0.00 | % MAD (24 hour Q) |
| TWO FORTY-ONE CREEK NEAR PENTICTON | 08NM241 | Natural | 4.50 | 0.06 | 0.00 | 1.63 | NaN | % MAD (24 hour Q) |
| TWO FORTY CREEK NEAR PENTICTON | 08NM240 | Natural | 4.94 | 0.06 | 0.00 | 2.96 | 0.00 | % MAD (24 hour Q) |
| WEST KETTLE RIVER NEAR MCCULLOCH | 08NN015 | Natural | 233.00 | 3.46 | 0.12 | 3.51 | 0.09 | % MAD (24 hour Q) |
| SPIUS CREEK BELOW SILVER CREEK | 08LG068 | Natural | 178.00 | 3.44 | 0.14 | 3.98 | 0.13 | % MAD (24 hour Q) |
| TULAMEEN RIVER BELOW VUICH CREEK | 08NL071 | Natural | 253.00 | 6.39 | 0.36 | 5.6 | 0.33 | % MAD (24 hour Q) |
| VASEUX CREEK ABOVE SOLCO CREEK | 08NM171 | Natural | 117.00 | 0.91 | 0.05 | 5.9 | 0.05 | % MAD (24 hour Q) |
| SIWASH CREEK NEAR PRINCETON | 08NL039 | Regulated | 263.00 | 1.37 | 0.08 | 5.94 | 0.08 | % MAD (24 hour Q) |
| COLDWATER RIVER AT MERRITT | 08LG010 | Regulated | 917.00 | 8.08 | 0.48 | 5.97 | 0.43 | % MAD (24 hour Q) |
| FISHTRAP CREEK NEAR MCLURE | 08LB024 | Natural | 135.00 | 0.79 | 0.05 | 6.05 | 0.05 | % MAD (24 hour Q) |
| HEDLEY CREEK NEAR THE MOUTH | 08NL050 | Natural | 388.00 | 2.48 | 0.15 | 6.09 | 0.13 | % MAD (24 hour Q) |
| INKANEEP CREEK NEAR THE MOUTH | 08NM200 | Regulated | 227.00 | 0.40 | 0.03 | 7.18 | 0.03 | % MAD (24 hour Q) |
| TULAMEEN RIVER AT PRINCETON | 08NL024 | Natural | 1780.00 | 21.77 | 1.61 | 7.38 | 1.50 | % MAD (24 hour Q) |
| SPIUS CREEK NEAR CANFORD | 08LG008 | Natural | 775.00 | 10.21 | 0.78 | 7.66 | 0.71 | % MAD (24 hour Q) |
| COLDWATER RIVER NEAR BROOKMERE | 08LG048 | Natural | 316.00 | 6.76 | 0.53 | 7.78 | 0.49 | % MAD (24 hour Q) |
| PEARSON CREEK NEAR THE MOUTH | 08NM172 | Natural | 73.60 | 0.97 | 0.08 | 7.83 | 0.07 | % MAD (24 hour Q) |
| LEMIEUX CREEK NEAR THE MOUTH | 08LB078 | Regulated | 443.00 | 3.15 | 0.26 | 8.28 | 0.23 | % MAD (24 hour Q) |
| PENNASK CREEK NEAR QUILCHENA | 08LG016 | Natural | 87.60 | 0.72 | 0.07 | 9.49 | 0.06 | % MAD (24 hour Q) |
| CAMP CREEK AT MOUTH NEAR THIRSK | 08NM134 | Natural | 34.60 | 0.15 | 0.01 | 9.87 | 0.01 | % MAD (24 hour Q) |
| SHATFORD CREEK NEAR PENTICTON | 08NM037 | Regulated | 101.00 | 0.39 | 0.04 | 10.47 | 0.04 | % MAD (24 hour Q) |
| CHASE CREEK ABOVE THE MOUTH | 08LE112 | Regulated | 297.00 | 1.59 | 0.17 | 10.68 | 0.15 | % MAD (24 hour Q) |
| CRISS CREEK NEAR SAVONA | 08LF007 | Regulated | 479.00 | 1.73 | 0.19 | 11.21 | 0.15 | % MAD (24 hour Q) |
| SIMILKAMEEN RIVER AT PRINCETON | 08NL007 | Natural | 1810.00 | 23.53 | 3.03 | 12.86 | 2.78 | % MAD (24 hour Q) |
| EAST CANOE CREEK ABOVE DAM | 08LE108 | Natural | 20.80 | 0.11 | 0.01 | 12.99 | 0.01 | % MAD (24 hour Q) |
| SIMILKAMEEN RIVER NEAR HEDLEY | 08NL038 | Natural | 5580.00 | 48.43 | 6.30 | 13.01 | 5.93 | % MAD (24 hour Q) |
| CAYOOSH CREEK NEAR LILLOOET | 08ME002 | Regulated | 885.00 | 12.92 | 1.73 | 13.42 | 1.63 | % MAD (24 hour Q) |
| WHITEMAN CREEK ABOVE BOULEAU CREEK | 08NM174 | Natural | 114.00 | 0.65 | 0.09 | 14.08 | 0.09 | % MAD (24 hour Q) |
| VERNON CREEK AT OUTLET OF KALAMALKA LAKE | 08NM065 | Regulated | 569.00 | 0.90 | 0.13 | 14.14 | 0.12 | % MAD (24 hour Q) |
| EWART CREEK NEAR CATHEDRAL PARK | 08NL076 | Natural | NA | 1.76 | 0.25 | 14.26 | 0.23 | % MAD (24 hour Q) |
| MISSION CREEK NEAR EAST KELOWNA | 08NM116 | Regulated | 795.00 | 6.20 | 0.94 | 15.16 | 0.86 | % MAD (24 hour Q) |
| SALMON RIVER AT FALKLAND | 08LE020 | Regulated | 1030.00 | 2.94 | 0.48 | 16.32 | 0.48 | % MAD (24 hour Q) |
| NICOLA RIVER NEAR SPENCES BRIDGE | 08LG006 | Regulated | 7100.00 | 26.51 | 4.36 | 16.46 | 4.18 | % MAD (24 hour Q) |
| SIMILKAMEEN RIVER ABOVE GOODFELLOW CREEK | 08NL070 | Natural | 408.00 | 7.78 | 1.31 | 16.87 | 1.24 | % MAD (24 hour Q) |
| ASHNOLA RIVER NEAR KEREMEOS | 08NL004 | Natural | 1050.00 | 7.85 | 1.46 | 18.65 | 1.37 | % MAD (24 hour Q) |
| HARPER CREEK NEAR THE MOUTH | 08LB076 | Natural | 166.00 | 4.03 | 0.77 | 19.21 | 0.69 | % MAD (24 hour Q) |
| SALMON RIVER NEAR SALMON ARM | 08LE021 | Regulated | 1550.00 | 5.08 | 1.00 | 19.61 | 0.99 | % MAD (24 hour Q) |
| PASAYTEN RIVER ABOVE CALCITE CREEK | 08NL069 | Natural | 566.00 | 8.07 | 1.59 | 19.68 | 1.50 | % MAD (24 hour Q) |
| BESSETTE CREEK ABOVE BEAVERJACK CREEK | 08LC039 | Regulated | 769.00 | 3.58 | 0.71 | 19.75 | 0.56 | % MAD (24 hour Q) |
The recommended mean weekly maximum temperature (which is the mean of the max daily temperatures from the last seven days) for the protection of all fish species should not exceed 20 degrees C and the maximum daily temperature should not exceed 23degrees C. Reaching either one of these thresholds may trigger fisheries closures and water use restrictions within the affected watersheds. Only a small subset of stations from the Water Survey of Canada collect temperature data in addition to streamflow data; thus the number of sites shown here is much smaller than for streamflow.
Map data was updated on 09 September 2021, 15:33 PM.
The table below shows stations with a 7-day maximum daily temperature (i.e., the max daily temperature from the past 7 days) above 20degC. Also shown are the days from the past week in which the maximum daily temperature exceeded either 20degC or 23degC (critical thresholds for fish health). If no sites are present, all sites with water temperature data show 7-day maximum daily temperatures below 20degC.
Regulation Status refers to whether flows are natural or regulated by human activities such as dams; this (as well as the Basin Area) were determined by the Water Survey of Canada.
Data was updated on 09 September 2021, 15:33 PM.
| Station Name | ID | Regulation Status | Basin Area (km2) | Mean Max Daily Temp (last 7 days; deg C) | Max temp over last 24 hours (degC) | Min temp over last 24 hours (degC) | Mean temp over last 24 hours (degC) | Dates above 20 degC in last 7 days | Dates above 23 degC in last 7 days |
|---|---|---|---|---|---|---|---|---|---|
| OKANAGAN RIVER AT PENTICTON | 08NM050 | Regulated | 5980 | 20.85 | 20.57 | 19.86 | 20.13 | Sep 03; Sep 04; Sep 05; Sep 06; Sep 07; Sep 08; Sep 09 | NA |
| KALAMALKA LAKE AT VERNON PUMPHOUSE | 08NM143 | NA | NA | 20.77 | 20.58 | 18.8 | 19.47 | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 | NA |
| OKANAGAN LAKE AT KELOWNA | 08NM083 | NA | NA | 20.21 | 20.24 | 19.23 | 19.6 | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 | NA |
| OKANAGAN RIVER NEAR OLIVER | 08NM085 | Regulated | 7540 | 20.2 | 19.85 | 17.95 | 19.01 | Sep 03; Sep 04; Sep 07; Sep 08 | NA |
The table below shows water temperatures specific to all of the lake sites within the region. If the 7-day maximum daily temperatures temperatures exceeded 20degC, data for the site is also included within the table previously.
| Station Name | ID | Mean Max Daily Temp (last 7 days; deg C) | Max temp over last 24 hours (degC) | Min temp over last 24 hours (degC) | Mean temp over last 24 hours (degC) | Dates above 20 degC in last 7 days | Dates above 23 degC in last 7 days |
|---|---|---|---|---|---|---|---|
| KALAMALKA LAKE AT VERNON PUMPHOUSE | 08NM143 | 20.77 | 20.58 | 18.80 | 19.47 | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 | NA |
| OKANAGAN LAKE AT KELOWNA | 08NM083 | 20.21 | 20.24 | 19.23 | 19.60 | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 | NA |
| NICOLA LAKE NEAR QUILCHENA | 08LG046 | 17.34 | 17.3 | 16.40 | 16.83 | NA | NA |
The following table contains all of the drought-relevant statistics for all stations within the region.
These statistics include:
Regulation Status refers to whether flows are natural or regulated by human activities such as dams; this (as well as the Basin Area) were determined by the Water Survey of Canada.
Data was updated on 09 September 2021, 15:33 PM.
| Station Name | ID | Record Length | Basin Area (km2) | Regulation Status | Last 24 hour Discharge (m3/s) | Percentile - Last 24 Hour Discharge | Percentile Category - Last 24 Hour Discharge | Latest 7 Day Discharge (m3/s) | Percentile - 7 Day Discharge | Percentile Category - 7 Day Discharge | Percent of Daily Mean 7 Day Discharge (%; Historic Mean 7 Day Discharge in m3/s) | Percent of Daily Median 7 Day Discharge (%; Historic Median 7 Day Discharge in m3/s) | Historic Min 7 Day Discharge (m3/s) | MAD (m3/s) | % MAD | MAD Category | % MAD (24 hour Q) | Mean Max Daily Temp (last 7 days; deg C) | Max temp over last 24 hours (degC) | Min temp over last 24 hours (degC) | Mean temp over last 24 hours (degC) | Dates above 23 degC in last 7 days | Dates above 20 degC in last 7 days |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| SEYMOUR RIVER NEAR SEYMOUR ARM | 08LE027 | 68 | 8.05e+02 | Natural | 10.50 | 0 | Low | 10.23 | 0 | Low | 39 (26.29) | 46 (26.29) | 11.89 | 36.40 | 28.1 | 20 to 100% | 28.83 | NA | NA | NA | NA | NA | NA |
| THOMPSON RIVER NEAR SAVONA | 08LF033 | 14 | 3.91e+04 | Natural | 380.02 | 0 | Low | 396.06 | 0 | Low | 58 (677.82) | 59 (677.82) | 520.71 | 696.11 | 56.9 | 20 to 100% | 54.59 | 18.1 | 18.1 | 17.90 | 17.98 | NA | NA |
| FRASER RIVER AT BIG BAR CREEK | 08MD013 | 38 | 1.46e+05 | Regulated | 987.69 | 0 | Low | 1039.48 | 0 | Low | 62 (1679.07) | 63 (1679.07) | 1070.00 | 1524.46 | 68.19 | 20 to 100% | 64.79 | 15.8 | 16.4 | 16.20 | 16.32 | NA | NA |
| HEDLEY CREEK NEAR THE MOUTH | 08NL050 | 48 | 3.88e+02 | Natural | 0.13 | 0 | Low | 0.15 | 0 | Low | 17 (0.89) | 20 (0.89) | 0.18 | 2.48 | 6.09 | 5 to 10% | 5.29 | NA | NA | NA | NA | NA | NA |
| CAMP CREEK AT MOUTH NEAR THIRSK | 08NM134 | 55 | 3.46e+01 | Natural | 0.01 | 0 | Low | 0.01 | 0 | Low | 29 (0.05) | 36 (0.05) | 0.02 | 0.15 | 9.87 | 5 to 10% | 9.70 | NA | NA | NA | NA | NA | NA |
| PEARSON CREEK NEAR THE MOUTH | 08NM172 | 18 | 7.36e+01 | Natural | 0.07 | 0 | Low | 0.08 | 0 | Low | 16 (0.49) | 22 (0.49) | 0.08 | 0.97 | 7.83 | 5 to 10% | 6.86 | NA | NA | NA | NA | NA | NA |
| CLEARWATER RIVER NEAR CLEARWATER STATION | 08LA001 | 83 | 1.03e+04 | Natural | 107.31 | 0 | Low | 112.75 | 2 | Much below normal (<10) | 54 (208.02) | 56 (208.02) | 105.14 | 224.90 | 50.13 | 20 to 100% | 47.71 | NA | NA | NA | NA | NA | NA |
| NORTH THOMPSON RIVER AT MCLURE | 08LB064 | 63 | 1.96e+04 | Natural | 212.77 | 2 | Much below normal (<10) | 218.63 | 0 | Low | 56 (387.05) | 58 (387.05) | 218.86 | 431.38 | 50.68 | 20 to 100% | 49.32 | 15.4 | 15.56 | 14.64 | 15.08 | NA | NA |
| FISHTRAP CREEK NEAR MCLURE | 08LB024 | 54 | 1.35e+02 | Natural | 0.05 | 2 | Much below normal (<10) | 0.05 | 2 | Much below normal (<10) | 19 (0.25) | 24 (0.25) | 0.03 | 0.79 | 6.05 | 5 to 10% | 6.10 | NA | NA | NA | NA | NA | NA |
| DENNIS CREEK NEAR 1780 METRE CONTOUR | 08NM242 | 35 | 3.73e+00 | Natural | 0.00 | 3 | Much below normal (<10) | 0.00 | 0 | Low | 0 (0.01) | 0 (0.01) | 0.00 | 0.05 | 0 | <1% | 0.00 | NA | NA | NA | NA | NA | NA |
| TWO FORTY CREEK NEAR PENTICTON | 08NM240 | 37 | 4.94e+00 | Natural | 0.00 | 3 | Much below normal (<10) | 0.00 | 3 | Much below normal (<10) | 18 (0.01) | 18 (0.01) | 0.00 | 0.06 | 2.96 | 1 to 5% | 3.22 | NA | NA | NA | NA | NA | NA |
| THOMPSON RIVER NEAR SPENCES BRIDGE | 08LF051 | 70 | 5.54e+04 | Natural | 405.13 | 3 | Much below normal (<10) | 422.87 | 3 | Much below normal (<10) | 63 (673.39) | 66 (673.39) | 395.71 | 779.99 | 54.22 | 20 to 100% | 51.94 | 19.38 | 19.57 | 18.73 | 19.09 | NA | NA |
| WEST KETTLE RIVER NEAR MCCULLOCH | 08NN015 | 65 | 2.33e+02 | Natural | 0.09 | 3 | Much below normal (<10) | 0.12 | 6 | Much below normal (<10) | 14 (0.86) | 28 (0.86) | 0.09 | 3.46 | 3.51 | 1 to 5% | 2.62 | NA | NA | NA | NA | NA | NA |
| VASEUX CREEK ABOVE SOLCO CREEK | 08NM171 | 49 | 1.17e+02 | Natural | 0.05 | 4 | Much below normal (<10) | 0.05 | 4 | Much below normal (<10) | 28 (0.19) | 38 (0.19) | 0.02 | 0.91 | 5.9 | 5 to 10% | 5.49 | NA | NA | NA | NA | NA | NA |
| FRASER RIVER ABOVE TEXAS CREEK | 08MF040 | 69 | 1.54e+05 | Regulated | 1084.22 | 4 | Much below normal (<10) | 1164.47 | 6 | Much below normal (<10) | 68 (1702.88) | 69 (1702.88) | 992.43 | 1736.56 | 67.06 | 20 to 100% | 62.44 | 15.99 | 16.58 | 16.32 | 16.39 | NA | NA |
| EWART CREEK NEAR CATHEDRAL PARK | 08NL076 | 23 | NA | Natural | 0.23 | 4 | Much below normal (<10) | 0.25 | 13 | Below Normal (10-24) | 44 (0.57) | 52 (0.57) | 0.18 | 1.76 | 14.26 | 10 to 20% | 13.10 | NA | NA | NA | NA | NA | NA |
| EAGLE RIVER NEAR MALAKWA | 08LE024 | 62 | 9.32e+02 | Natural | 12.15 | 6 | Much below normal (<10) | 12.30 | 3 | Much below normal (<10) | 49 (25.26) | 60 (25.26) | 10.97 | 38.00 | 32.37 | 20 to 100% | 31.97 | NA | NA | NA | NA | NA | NA |
| INKANEEP CREEK NEAR THE MOUTH | 08NM200 | 15 | 2.27e+02 | Regulated | 0.03 | 7 | Much below normal (<10) | 0.03 | 7 | Much below normal (<10) | 58 (0.05) | 72 (0.05) | 0.03 | 0.40 | 7.18 | 5 to 10% | 6.96 | 19 | 18.76 | 14.23 | 16.59 | NA | NA |
| SALMON RIVER AT FALKLAND | 08LE020 | 78 | 1.03e+03 | Regulated | 0.48 | 8 | Much below normal (<10) | 0.48 | 6 | Much below normal (<10) | 42 (1.14) | 44 (1.14) | 0.29 | 2.94 | 16.32 | 10 to 20% | 16.37 | NA | NA | NA | NA | NA | NA |
| SIMILKAMEEN RIVER AT PRINCETON | 08NL007 | 85 | 1.81e+03 | Natural | 2.78 | 10 | Much below normal (<10) | 3.03 | 12 | Below Normal (10-24) | 53 (5.76) | 59 (5.76) | 2.06 | 23.53 | 12.86 | 10 to 20% | 11.80 | NA | NA | NA | NA | NA | NA |
| HARPER CREEK NEAR THE MOUTH | 08LB076 | 47 | 1.66e+02 | Natural | 0.69 | 11 | Below Normal (10-24) | 0.77 | 13 | Below Normal (10-24) | 46 (1.68) | 58 (1.68) | 0.39 | 4.03 | 19.21 | 10 to 20% | 17.01 | 11.36 | 10.7 | 9.40 | 10.08 | NA | NA |
| TULAMEEN RIVER BELOW VUICH CREEK | 08NL071 | 46 | 2.53e+02 | Natural | 0.33 | 11 | Below Normal (10-24) | 0.36 | 17 | Below Normal (10-24) | 38 (0.93) | 46 (0.93) | 0.18 | 6.39 | 5.6 | 5 to 10% | 5.16 | NA | NA | NA | NA | NA | NA |
| SOUTH THOMPSON RIVER AT CHASE | 08LE031 | 97 | 1.58e+04 | Natural | 157.19 | 12 | Below Normal (10-24) | 164.87 | 14 | Below Normal (10-24) | 69 (237.75) | 73 (237.75) | 132.29 | 294.63 | 55.96 | 20 to 100% | 53.35 | 19.63 | 19.1 | 17.80 | 18.27 | NA | Sep 07; Sep 08 |
| CLARK CREEK NEAR WINFIELD | 08NM146 | 23 | 1.53e+01 | Natural | 0.00 | 13 | Below Normal (10-24) | 0.00 | 17 | Below Normal (10-24) | 10 (0.01) | Inf (0.01) | 0.00 | 0.08 | 1.27 | 1 to 5% | 1.27 | NA | NA | NA | NA | NA | NA |
| TULAMEEN RIVER AT PRINCETON | 08NL024 | 69 | 1.78e+03 | Natural | 1.50 | 14 | Below Normal (10-24) | 1.61 | 16 | Below Normal (10-24) | 47 (3.43) | 54 (3.43) | 0.87 | 21.77 | 7.38 | 5 to 10% | 6.88 | NA | NA | NA | NA | NA | NA |
| COLDWATER RIVER NEAR BROOKMERE | 08LG048 | 56 | 3.16e+02 | Natural | 0.49 | 14 | Below Normal (10-24) | 0.53 | 18 | Below Normal (10-24) | 50 (1.06) | 59 (1.06) | 0.35 | 6.76 | 7.78 | 5 to 10% | 7.19 | NA | NA | NA | NA | NA | NA |
| ADAMS RIVER NEAR SQUILAX | 08LD001 | 110 | 3.21e+03 | Natural | 51.40 | 15 | Below Normal (10-24) | 53.56 | 15 | Below Normal (10-24) | 74 (72.08) | 80 (72.08) | 27.91 | 71.22 | 75.21 | 20 to 100% | 72.17 | NA | NA | NA | NA | NA | NA |
| LEMIEUX CREEK NEAR THE MOUTH | 08LB078 | 43 | 4.43e+02 | Regulated | 0.23 | 15 | Below Normal (10-24) | 0.26 | 15 | Below Normal (10-24) | 26 (1) | 36 (1) | 0.01 | 3.15 | 8.28 | 5 to 10% | 7.31 | 15.97 | 14.59 | 12.06 | 13.32 | NA | NA |
| EAST CANOE CREEK ABOVE DAM | 08LE108 | 35 | 2.08e+01 | Natural | 0.01 | 15 | Below Normal (10-24) | 0.01 | 17 | Below Normal (10-24) | 47 (0.03) | 70 (0.03) | 0.00 | 0.11 | 12.99 | 10 to 20% | 12.10 | NA | NA | NA | NA | NA | NA |
| PENNASK CREEK NEAR QUILCHENA | 08LG016 | 78 | 8.76e+01 | Natural | 0.06 | 15 | Below Normal (10-24) | 0.07 | 18 | Below Normal (10-24) | 33 (0.21) | 57 (0.21) | 0.02 | 0.72 | 9.49 | 5 to 10% | 8.51 | NA | NA | NA | NA | NA | NA |
| SHUSWAP RIVER NEAR ENDERBY | 08LC002 | 86 | 4.72e+03 | Regulated | 32.08 | 16 | Below Normal (10-24) | 30.03 | 11 | Below Normal (10-24) | 62 (48.45) | 70 (48.45) | 26.84 | 88.26 | 34.02 | 20 to 100% | 36.35 | NA | NA | NA | NA | NA | NA |
| MISSION CREEK NEAR EAST KELOWNA | 08NM116 | 69 | 7.95e+02 | Regulated | 0.86 | 16 | Below Normal (10-24) | 0.94 | 20 | Below Normal (10-24) | 40 (2.38) | 57 (2.38) | 0.51 | 6.20 | 15.16 | 10 to 20% | 13.84 | NA | NA | NA | NA | NA | NA |
| SPIUS CREEK NEAR CANFORD | 08LG008 | 55 | 7.75e+02 | Natural | 0.71 | 17 | Below Normal (10-24) | 0.78 | 15 | Below Normal (10-24) | 49 (1.59) | 65 (1.59) | 0.29 | 10.21 | 7.66 | 5 to 10% | 7.00 | 16.38 | 17.06 | 13.55 | 15.14 | NA | NA |
| ASHNOLA RIVER NEAR KEREMEOS | 08NL004 | 78 | 1.05e+03 | Natural | 1.37 | 17 | Below Normal (10-24) | 1.46 | 22 | Below Normal (10-24) | 49 (3.02) | 59 (3.02) | 0.62 | 7.85 | 18.65 | 10 to 20% | 17.43 | NA | NA | NA | NA | NA | NA |
| NICOLA RIVER AT OUTLET OF NICOLA LAKE | 08LG065 | 38 | 2.96e+03 | Regulated | 1.74 | 18 | Below Normal (10-24) | 1.74 | 8 | Much below normal (<10) | 72 (2.41) | 75 (2.41) | 0.99 | 5.33 | 32.6 | 20 to 100% | 32.70 | 17.25 | 18.64 | 17.12 | 17.85 | NA | NA |
| BESSETTE CREEK ABOVE BEAVERJACK CREEK | 08LC039 | 49 | 7.69e+02 | Regulated | 0.56 | 18 | Below Normal (10-24) | 0.71 | 27 | Normal (25-75) | 50 (1.42) | 67 (1.42) | 0.19 | 3.58 | 19.75 | 10 to 20% | 15.59 | 15.84 | 15.23 | 13.73 | 14.52 | NA | NA |
| NICOLA RIVER AT OUTLET OF DOUGLAS LAKE | 08LG028 | 7 | 1.30e+03 | Regulated | 0.02 | 20 | Below Normal (10-24) | 0.02 | 20 | Below Normal (10-24) | 10 (0.22) | 12 (0.22) | 0.01 | 5.65 | 0.37 | <1% | 0.42 | NA | NA | NA | NA | NA | NA |
| SIMILKAMEEN RIVER NEAR HEDLEY | 08NL038 | 55 | 5.58e+03 | Natural | 5.93 | 20 | Below Normal (10-24) | 6.30 | 20 | Below Normal (10-24) | 61 (10.31) | 69 (10.31) | 3.34 | 48.43 | 13.01 | 10 to 20% | 12.24 | NA | NA | NA | NA | NA | NA |
| CAYOOSH CREEK NEAR LILLOOET | 08ME002 | 74 | 8.85e+02 | Regulated | 1.63 | 21 | Below Normal (10-24) | 1.73 | 26 | Normal (25-75) | 21 (8.24) | 71 (8.24) | 0.31 | 12.92 | 13.42 | 10 to 20% | 12.64 | NA | NA | NA | NA | NA | NA |
| NICOLA RIVER NEAR SPENCES BRIDGE | 08LG006 | 73 | 7.10e+03 | Regulated | 4.18 | 21 | Below Normal (10-24) | 4.36 | 27 | Normal (25-75) | 67 (6.49) | 78 (6.49) | 2.75 | 26.51 | 16.46 | 10 to 20% | 15.77 | 14.41 | 14.98 | 14.14 | 14.61 | NA | NA |
| COLDWATER RIVER AT MERRITT | 08LG010 | 60 | 9.17e+02 | Regulated | 0.43 | 22 | Below Normal (10-24) | 0.48 | 28 | Normal (25-75) | 47 (1.02) | 56 (1.02) | 0.13 | 8.08 | 5.97 | 5 to 10% | 5.30 | 18.97 | 20.4 | 15.00 | 17.33 | NA | Sep 08; Sep 09 |
| DEADMAN RIVER ABOVE CRISS CREEK | 08LF027 | 67 | 8.78e+02 | Regulated | 0.53 | 23 | Below Normal (10-24) | 0.56 | 20 | Below Normal (10-24) | 67 (0.84) | 69 (0.84) | 0.10 | 1.89 | 29.56 | 20 to 100% | 27.97 | 17.01 | 16.7 | 12.60 | 14.29 | NA | NA |
| SHATFORD CREEK NEAR PENTICTON | 08NM037 | 64 | 1.01e+02 | Regulated | 0.04 | 23 | Below Normal (10-24) | 0.04 | 21 | Below Normal (10-24) | 40 (0.1) | 51 (0.1) | 0.01 | 0.39 | 10.47 | 10 to 20% | 9.89 | NA | NA | NA | NA | NA | NA |
| BLUE RIVER NEAR BLUE RIVER | 08LB038 | 40 | 2.72e+02 | Natural | 3.31 | 23 | Below Normal (10-24) | 3.69 | 26 | Normal (25-75) | 64 (5.8) | 77 (5.8) | 2.41 | 10.85 | 34.01 | 20 to 100% | 30.50 | NA | NA | NA | NA | NA | NA |
| BARRIERE RIVER AT THE MOUTH | 08LB020 | 80 | 1.14e+03 | Natural | 3.11 | 23 | Below Normal (10-24) | 3.27 | 29 | Normal (25-75) | 65 (5.03) | 81 (5.03) | 1.50 | 14.69 | 22.24 | 20 to 100% | 21.14 | NA | NA | NA | NA | NA | NA |
| YALAKOM RIVER ABOVE ORE CREEK | 08ME025 | 37 | 5.81e+02 | Natural | 3.56 | 24 | Normal (25-75) | 3.48 | 8 | Much below normal (<10) | 78 (4.44) | 83 (4.44) | 3.11 | 4.45 | 78.22 | 20 to 100% | 79.90 | NA | NA | NA | NA | NA | NA |
| PASAYTEN RIVER ABOVE CALCITE CREEK | 08NL069 | 45 | 5.66e+02 | Natural | 1.50 | 24 | Normal (25-75) | 1.59 | 24 | Normal (25-75) | 62 (2.57) | 74 (2.57) | 0.85 | 8.07 | 19.68 | 10 to 20% | 18.61 | NA | NA | NA | NA | NA | NA |
| CHASE CREEK ABOVE THE MOUTH | 08LE112 | 21 | 2.97e+02 | Regulated | 0.15 | 24 | Below Normal (10-24) | 0.17 | 43 | Normal (25-75) | 71 (0.24) | 85 (0.24) | 0.01 | 1.59 | 10.68 | 10 to 20% | 9.57 | NA | NA | NA | NA | NA | NA |
| OKANAGAN RIVER NEAR OLIVER | 08NM085 | 74 | 7.54e+03 | Regulated | 10.70 | 26 | Normal (25-75) | 10.69 | 25 | Normal (25-75) | 60 (17.76) | 75 (17.76) | 2.45 | 19.34 | 55.29 | 20 to 100% | 55.30 | 20.2 | 19.85 | 17.95 | 19.01 | NA | Sep 03; Sep 04; Sep 07; Sep 08 |
| SALMON RIVER NEAR SALMON ARM | 08LE021 | 61 | 1.55e+03 | Regulated | 0.99 | 27 | Normal (25-75) | 1.00 | 25 | Normal (25-75) | 60 (1.67) | 68 (1.67) | 0.29 | 5.08 | 19.61 | 10 to 20% | 19.53 | NA | NA | NA | NA | NA | NA |
| SIWASH CREEK NEAR PRINCETON | 08NL039 | 36 | 2.63e+02 | Regulated | 0.08 | 28 | Normal (25-75) | 0.08 | 28 | Normal (25-75) | 48 (0.17) | 62 (0.17) | 0.01 | 1.37 | 5.94 | 5 to 10% | 5.73 | NA | NA | NA | NA | NA | NA |
| SIMILKAMEEN RIVER ABOVE GOODFELLOW CREEK | 08NL070 | 46 | 4.08e+02 | Natural | 1.24 | 29 | Normal (25-75) | 1.31 | 33 | Normal (25-75) | 68 (1.93) | 80 (1.93) | 0.54 | 7.78 | 16.87 | 10 to 20% | 15.94 | NA | NA | NA | NA | NA | NA |
| BESSETTE CREEK ABOVE LUMBY LAGOON OUTFALL | 08LC042 | 48 | 6.32e+02 | Regulated | 0.62 | 31 | Normal (25-75) | 0.71 | 38 | Normal (25-75) | 57 (1.23) | 80 (1.23) | 0.22 | 3.10 | 22.72 | 20 to 100% | 19.85 | 16.63 | 15.8 | 13.40 | 14.69 | NA | NA |
| NORTH THOMPSON RIVER AT BIRCH ISLAND | 08LB047 | 61 | 4.49e+03 | Natural | 114.61 | 33 | Normal (25-75) | 103.09 | 8 | Much below normal (<10) | 66 (155.16) | 71 (155.16) | 88.84 | 151.92 | 67.86 | 20 to 100% | 75.44 | NA | NA | NA | NA | NA | NA |
| QUILCHENA CREEK AT QUILCHENA | 08LG017 | 12 | 7.87e+02 | Regulated | 0.07 | 33 | Normal (25-75) | 0.09 | 25 | Normal (25-75) | 56 (0.16) | 56 (0.16) | 0.00 | NA | NA | Not ranked | NA | NA | NA | NA | NA | NA | NA |
| OKANAGAN RIVER AT PENTICTON | 08NM050 | 100 | 5.98e+03 | Regulated | 11.55 | 35 | Normal (25-75) | 11.61 | 33 | Normal (25-75) | 68 (17.08) | 80 (17.08) | 1.90 | 15.82 | 73.37 | 20 to 100% | 73.00 | 20.85 | 20.57 | 19.86 | 20.13 | NA | Sep 03; Sep 04; Sep 05; Sep 06; Sep 07; Sep 08; Sep 09 |
| SPIUS CREEK BELOW SILVER CREEK | 08LG068 | 17 | 1.78e+02 | Natural | 0.13 | 35 | Normal (25-75) | 0.14 | 35 | Normal (25-75) | 65 (0.21) | 98 (0.21) | 0.02 | 3.44 | 3.98 | 1 to 5% | 3.80 | NA | NA | NA | NA | NA | NA |
| OKANAGAN RIVER AT OKANAGAN FALLS | 08NM002 | 105 | 6.72e+03 | Regulated | 11.85 | 37 | Normal (25-75) | 11.87 | 37 | Normal (25-75) | 74 (16.13) | 84 (16.13) | 1.94 | 16.59 | 71.58 | 20 to 100% | 71.47 | 19.93 | 20.02 | 19.25 | 19.56 | NA | Sep 07; Sep 08; Sep 09 |
| CRISS CREEK NEAR SAVONA | 08LF007 | 69 | 4.79e+02 | Regulated | 0.15 | 41 | Normal (25-75) | 0.19 | 55 | Normal (25-75) | 41 (0.47) | 108 (0.47) | 0.00 | 1.73 | 11.21 | 10 to 20% | 8.81 | NA | NA | NA | NA | NA | NA |
| VERNON CREEK AT OUTLET OF KALAMALKA LAKE | 08NM065 | 64 | 5.69e+02 | Regulated | 0.12 | 50 | Normal (25-75) | 0.13 | 47 | Normal (25-75) | 31 (0.41) | 98 (0.41) | 0.00 | 0.90 | 14.14 | 10 to 20% | 13.84 | NA | NA | NA | NA | NA | NA |
| HURLEY RIVER BELOW LONE GOAT CREEK | 08ME027 | 25 | 3.12e+02 | Natural | 11.18 | 60 | Normal (25-75) | 8.36 | 0 | Low | 70 (12.01) | 72 (12.01) | 8.07 | 13.43 | 62.25 | 20 to 100% | 83.21 | NA | NA | NA | NA | NA | NA |
| WHITEMAN CREEK ABOVE BOULEAU CREEK | 08NM174 | 48 | 1.14e+02 | Natural | 0.09 | 60 | Normal (25-75) | 0.09 | 53 | Normal (25-75) | 83 (0.11) | 131 (0.11) | 0.01 | 0.65 | 14.08 | 10 to 20% | 13.35 | NA | NA | NA | NA | NA | NA |
| BONAPARTE RIVER BELOW CACHE CREEK | 08LF002 | 59 | 5.02e+03 | Regulated | 3.76 | 62 | Normal (25-75) | 3.87 | 61 | Normal (25-75) | 115 (3.38) | 128 (3.38) | 0.29 | 5.92 | 65.35 | 20 to 100% | 63.42 | 14.07 | 14.2 | 14.10 | 14.17 | NA | NA |
| GUICHON CREEK ABOVE TUNKWA LAKE DIVERSION | 08LG056 | 53 | 7.82e+01 | Natural | 0.05 | 63 | Normal (25-75) | 0.05 | 60 | Normal (25-75) | 86 (0.06) | 104 (0.06) | 0.01 | 0.16 | 32.4 | 20 to 100% | 32.17 | NA | NA | NA | NA | NA | NA |
| SETON RIVER NEAR LILLOOET | 08ME003 | 79 | 1.02e+03 | Regulated | 32.04 | 74 | Normal (25-75) | 31.23 | 71 | Normal (25-75) | 105 (29.62) | 149 (29.62) | 6.10 | 23.47 | 133.04 | > 100% | 136.52 | NA | NA | NA | NA | NA | NA |
| GUICHON CREEK AT OUTLET OF MAMIT LAKE | 08LG041 | 48 | 8.71e+02 | Regulated | 0.55 | 74 | Normal (25-75) | 0.57 | 72 | Normal (25-75) | 125 (0.46) | 155 (0.46) | 0.06 | 0.95 | 60.26 | 20 to 100% | 57.86 | NA | NA | NA | NA | NA | NA |
| BRIDGE RIVER (SOUTH BRANCH) BELOW BRIDGE GLACIER | 08ME023 | 42 | 1.44e+02 | Natural | 36.26 | 85 | Above normal (76-90) | 26.72 | 46 | Normal (25-75) | 93 (28.68) | 98 (28.68) | 13.94 | 12.85 | 207.89 | > 100% | 282.14 | 7.55 | 6.71 | 6.21 | 6.40 | NA | NA |
| BRIDGE RIVER ABOVE DOWNTON LAKE | 08ME028 | 25 | 7.08e+02 | Natural | 77.09 | 88 | Above normal (76-90) | 54.70 | 48 | Normal (25-75) | 91 (60.35) | 101 (60.35) | 36.66 | 36.75 | 148.86 | > 100% | 209.79 | NA | NA | NA | NA | NA | NA |
| VANCE CREEK BELOW DEAFIES CREEK | 08LC040 | 50 | 7.09e+01 | Natural | 0.25 | 88 | Above normal (76-90) | 0.23 | 82 | Above normal (76-90) | 162 (0.14) | 227 (0.14) | 0.02 | 0.49 | 46 | 20 to 100% | 51.17 | NA | NA | NA | NA | NA | NA |
| SHUSWAP RIVER NEAR LUMBY | 08LC003 | 83 | 2.00e+03 | Regulated | 38.73 | 91 | Much above normal (>90) | 40.84 | 89 | Above normal (76-90) | 142 (28.75) | 151 (28.75) | 14.71 | 50.70 | 80.55 | 20 to 100% | 76.40 | NA | NA | NA | NA | NA | NA |
| SHUSWAP RIVER AT OUTLET OF SUGAR LAKE RESERVOIR | 08LC018 | 58 | 1.13e+03 | Regulated | 31.35 | 91 | Much above normal (>90) | 33.28 | 91 | Much above normal (>90) | 146 (22.8) | 162 (22.8) | 11.59 | 39.01 | 85.29 | 20 to 100% | 80.34 | NA | NA | NA | NA | NA | NA |
| ARROWSTONE CREEK NEAR THE MOUTH | 08LF099 | 16 | 5.05e+01 | Natural | 0.06 | 94 | Much above normal (>90) | 0.06 | 100 | High | 191 (0.03) | 143 (0.03) | 0.02 | 0.11 | 52.04 | 20 to 100% | 54.07 | NA | NA | NA | NA | NA | NA |
| TWO FORTY-ONE CREEK NEAR PENTICTON | 08NM241 | 37 | 4.50e+00 | Natural | NaN | NA | Not ranked | 0.00 | 11 | Below Normal (10-24) | 9 (0.01) | 9 (0.01) | 0.00 | 0.06 | 1.63 | 1 to 5% | NaN | NA | NA | NA | NA | NA | NA |
| THOMPSON RIVER AT KAMLOOPS | 08LF023 | 4 | 3.78e+04 | Natural | NaN | NA | Not ranked | NaN | NA | Not ranked | NaN (636.04) | NaN (636.04) | 476.86 | NA | NaN | Not ranked | NaN | NA | NA | NA | NA | NA | NA |
| COLDSTREAM CREEK ABOVE MUNICIPAL INTAKE | 08NM142 | 48 | 6.06e+01 | Natural | NA | NA | Not ranked | NA | NA | NA | NA (0.09) | NA (0.09) | 0.01 | 0.25 | NA | Not ranked | NA | NA | NA | NA | NA | NA | NA |
| OKANAGAN RIVER BELOW MCINTYRE DAM | 08NM247 | 5 | 7.15e+03 | Regulated | 8.70 | NA | Not ranked | 8.70 | NA | Not ranked | 64 (13.65) | 86 (13.65) | 7.11 | 20.29 | 42.89 | 20 to 100% | 42.89 | 19.91 | 20.1 | 18.90 | 19.31 | NA | Sep 03; Sep 04; Sep 07; Sep 08; Sep 09 |
| NICOLA LAKE NEAR QUILCHENA | 08LG046 | NA | NA | NA | NA | NA | NA | NA | NA | NA | NA (NA) | NA (NA) | NA | NA | NA | Not ranked | NA | 17.34 | 17.3 | 16.40 | 16.83 | NA | NA |
| OKANAGAN LAKE AT KELOWNA | 08NM083 | NA | NA | NA | NA | NA | NA | NA | NA | NA | NA (NA) | NA (NA) | NA | NA | NA | Not ranked | NA | 20.21 | 20.24 | 19.23 | 19.60 | NA | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 |
| KALAMALKA LAKE AT VERNON PUMPHOUSE | 08NM143 | NA | NA | NA | NA | NA | NA | NA | NA | NA | NA (NA) | NA (NA) | NA | NA | NA | Not ranked | NA | 20.77 | 20.58 | 18.80 | 19.47 | NA | Sep 03; Sep 04; Sep 06; Sep 07; Sep 08; Sep 09 |